Invasion biology of Ponto-Caspian onychopod cladocerans (Crustacea: Cladocera: Onychopoda)

Panov, Vadim E.; Родионова, Н. В.; Bolshagin, P. V.; Bychek, Eugene A.

doi:10.1007/s10750-007-0752-0

Cited by 31 publications

(14 citation statements)

References 47 publications

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“…For example, invasive predatory onychopods have significantly reduced zooplankton species richness in the Great Lakes of North America (Yan et al, 2002) o n l y -group (Belyaeva and Taylor, 2009). o n l y (Gorokhova et al, 2000), and in a large artificial reservoir on the Volga River, Russia (Panov et al, 2007). The most famous cladoceran invaders are species of Daphnia.…”

Section: Discussionmentioning

confidence: 99%

Establishment of Chydorus sphaericus (O.F. Muller, 1785) (Crustacea: Cladocera) in Australia: consequences of mass fish stocking from Northern Europe?

Sharma

Kotov

2014

J Limnol

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Section: Discussionmentioning

confidence: 99%

Establishment of Chydorus sphaericus (O.F. Muller, 1785) (Crustacea: Cladocera) in Australia: consequences of mass fish stocking from Northern Europe?

Sharma

Kotov

2014

J Limnol

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“…Also, because the models (especially those derived from CT) identify thresholds, they may serve as useful predictors for shifting environmental factors. It has been recently demonstrated that, like many other organisms, zooplankton are affected by climate change (e.g., southern species and assemblages moving into northern regions- Beaugrand et al 2002;Panov et al 2007;Sullivan et al 2007). A warming climate is also projected to increase salinity in estuaries and coastal areas, with accompanying changes in the likelihood of non-native species becoming established (Rahel and Olden 2008).…”

Section: Discussionmentioning

confidence: 99%

Modelling physico-chemical factors affecting occurrences of a non-indigenous planktonic copepod in northeast Pacific estuaries

2009

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Estuarine ecosystems along the Pacific coast of North America are vulnerable to invasions by non-indigenous planktonic copepods, with documented invasions by at least nine species introduced via ship's ballast. One of these, the calanoid copepod Pseudodiaptomus inopinus, now occurs in a relatively wide geographical area in coastal estuaries of Washington and Oregon States. Although it appears to be well established in the region, plankton surveys conducted in 1992, 1996, 2000, and 2004 in estuaries from southern Vancouver Island in British Columbia, Canada, to northern California, United States indicate that it has not expanded its range. This static distribution suggests that P. inopinus has reached a distributional limit, and it may thus be a good organism for applying models for predicting planktonic invasions, by characterizing estuaries with and without populations of the copepod. In this study, we applied both parametric, linear (discriminant function analysis, logistic regression) and nonparametric, nonlinear (classification trees) techniques to develop models for occurrence of P. inopinus, to identify parameters that may lead to successful invasions and to identify specific estuaries or regions that might be at risk of invasion by this species. Both model types had similar results, identifying relatively simple salinity-and stratification-based models as good predictors of P. inopinus. While different models selected slightly different sets of variables and thresholds, all models identified relatively low salinity and stratification of water column temperature and salinity as important predictors of P. inopinus presence. The models also identified several ''false positives'' that mainly occurred in more inland waters of Puget Sound-estuaries that did not have P. inopinus, but had the conditions that support it, and which may be at risk for future invasions by this species.

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“…5; Table S1). In contrast to C. pengoi, E. anonyx has no prior invasion history in freshwater (Panov et al 2007) and is encountered in quite a narrow range of salinities in its native origin (Table S1). Both species prefer warm waters but are adapted to wide fluctuations in temperature in their native areas (Rivier 1998).…”

Section: Onychopod Cladoceransmentioning

confidence: 99%

“…have become more abundant in the Gulf of Finland and Gulf of Riga during recent decades and this has been partially accounted for mild winters and warmer summers. Panov et al (2007) have suggested that non-indigenous zooplankton species have positively responded to changes in climatic conditions of the recent past, allowing these species to reproduce and establish in the Baltic Sea. However, no studies on the impacts of both temperature and salinity changes on multiple non-indigenous species, have been published for the Baltic Sea, although many native species have been assessed for future changes (Vuorinen et al 2015).…”

Section: Introductionmentioning

confidence: 99%

Impacts of changing climate on the non-indigenous invertebrates in the northern Baltic Sea by end of the twenty-first century

et al. 2016

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Biological invasions coupled with climate change drive changes in marine biodiversity. Warming climate and changes in hydrology may either enable or hinder the spread of non-indigenous species (NIS) and little is known about how climate change modifies the richness and impacts of NIS in specific sea areas. We calculated from climate change simulations (RCO-SCOBI model) the changes in summer time conditions which northern Baltic Sea may to go through by the end of the twenty-first century, e.g., 2-5°C sea surface temperature rise and even up to 1.75 unit decrease in salinity. We reviewed the temperature and salinity tolerances (i.e., physiological tolerances and occurrence ranges in the field) of pelagic and benthic NIS established in-or with dispersal potential to-the northern Baltic Sea, and assessed how climate change will likely affect them. Our findings suggest a future decrease in barnacle larvae and an increase in Ponto-Caspian cladocerans in the pelagic community. In benthos, polychaetes, gastropods and decapods may become less abundant. By contrast, dreissenid bivalves, amphipods and mysids are expected to widen their distribution and increase in abundance in the coastal areas of the northern Baltic Sea. Potential salinity decrease acts as a major driver for NIS biogeography in the northern Baltic Sea, but temperature increase and extended summer season allow higher reproduction success in bivalves, zooplankton, amphipods and mysids. Successful NIS, i.e., coastal crustacean and bivalve species, pose a risk to native biota, as many of them have already demonstrated harmful effects in the Baltic Sea.Electronic supplementary material The online version of this article

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Invasion biology of Ponto-Caspian onychopod cladocerans (Crustacea: Cladocera: Onychopoda)

Abstract: We review the patterns of recent range expansions and the biology of the invasive PontoCaspian predatory onychopod cladocerans: Cercopagis pengoi, Evadne anonyx, Podonevadne trigona, Cornigerius maeoticus and Cornigerius bicornis.

Cited by 31 publications

References 47 publications

Establishment of Chydorus sphaericus (O.F. Muller, 1785) (Crustacea: Cladocera) in Australia: consequences of mass fish stocking from Northern Europe?

Establishment of Chydorus sphaericus (O.F. Muller, 1785) (Crustacea: Cladocera) in Australia: consequences of mass fish stocking from Northern Europe?

Modelling physico-chemical factors affecting occurrences of a non-indigenous planktonic copepod in northeast Pacific estuaries

Impacts of changing climate on the non-indigenous invertebrates in the northern Baltic Sea by end of the twenty-first century

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